Comparisons of energy reserves among strains of
Tribolium
castaneum
selected for resistance to hypoxia and
hypercarbia, and the unselected strain
E.J. Donahaye*, S. Navarro
Department of Stored Products, Agricultural Research Organization, The Volcani Center, P.O.B. 6, Bet Dagan, Israel
Accepted 27 July 1999
Abstract
The quantities of energy reserves and their utilization were examined in adults of three strains of
Tribolium castaneum (Herbst) before and during exposure to two modi®ed atmospheres. It was shown that a strain selected for resistance to high carbon dioxide (CO2) content (HCC) contained signi®cantly
greater triacylglycerol (TG) reserves than a strain selected for resistance to low oxygen (O2)
concentration (LOC) and an unselected strain. During exposure to HCC (65% CO2, 20% O2, balance
nitrogen), the major energy sources were TGs, most of which were consumed during exposure; TG utilization by the unselected strain was more rapid than that by the HCC-selected strain. During exposure to LOC (0.5% O2, 99.5% nitrogen), TGs were also utilized, but to a lesser extent, revealing an
indication of more attenuated mobilization of energy reserves. Here, too, TG utilization by the unselected strain was more rapid than by the LOC-selected strain. The function of TGs in enabling the insects to maintain their water balance during exposure was considered.
Concentrations of polysaccharides and glucose were low in all strains and although they decreased during exposure to MAs, their contribution to metabolic energy supply during exposure was small.72000 Elsevier Science Ltd. All rights reserved.
Keywords: Tribolium castaneum; Resistance; Hypoxia; Hypercarbia; Energy reserves
0022-474X/00/$ - see front matter72000 Elsevier Science Ltd. All rights reserved. PII: S 0 0 2 2 - 4 7 4 X ( 9 9 ) 0 0 0 4 4 - 2
www.elsevier.com/locate/jspr
* Corresponding author. Fax: +972-3-9604428.
1. Introduction
A non-toxic and environmentally benign alternative to fumigation for the control of insects in stored products is the use of modi®ed atmospheres (MAs). These are obtained by changing the proportions of the atmospheric gases within the storage container to atmospheres rich in carbon dioxide (CO2), poor in oxygen (O2) or a combination of both. Sensitivities of
stored-product insects to MAs have been widely studied (Annis, 1987) and MA insect control procedures have been put into practice (Delmenico, 1993). Their potential for more widespread use has been reviewed by Bell and Armitage (1992), and Longsta (1994), and further impetus is being provided by the forthcoming phase-out of methyl bromide (UNEP, 1995) and pressures to limit the use of phosphine, the remaining principal fumigant (Banks, 1994; EPA, 1998).
The development of insect resistance to fumigants has prompted laboratory studies on the acquisition of resistance to MAs (Bond and Buckland, 1979; Navarro et al., 1985). In a study using the ¯our beetle Tribolium castaneum (Herbst), (Donahaye, 1990a,b), a laboratory strain was selected for resistance to hypoxia and another for resistance to hypercarbia. Further studies showed that both selected strains were signi®cantly heavier than the unselected strain (Donahaye, 1993). These ®ndings together with those on rates of weight loss during exposure (Donahaye, 1992), led to this investigation into the nature of energy reserves, quantitative dierences in these reserves between the strains, and rates at which these were utilized during exposure to MAs.
It is known that fat tissue represents a considerable proportion of the body weight of pupae and adults of the ¯our beetle. Villeneuve and Lemonde (1963) recorded that lipids form up to 20% of the wet body weight in Tribolium confusum du Val and that they are the major source of energy during metamorphosis. Gilbert (1967) noted that triacylglycerols (TGs) form an important energy source for insects. These undergo hydrolysis to produce fatty acids which release further energy by oxidation. Kennington and Cannell (1967) showed that during exposure of Tribolium pupae to anoxia, lipids did not provide an energy source; however, as soon as the insects were returned to air, they were utilized in quantity. The accepted belief is that carbohydrate reserves in insects are utilized by the glycolytic pathway during anaerobic metabolism, but little information is available in the literature on lipid and carbohydrate metabolism under stress from hypoxia or hypercarbia.
The function of TGs in the conservation of the water balance in insects has been discussed by Edney (1967) and by Wigglesworth (1972). Friedlander and Navarro (1979a) examined the in¯uence of CO2 on TG metabolism in Ephestia cautella (Walker) pupae, to determine whether
water production from TG metabolism forms a regulatory mechanism to recompense for increased water loss due to the in¯uence of CO2 on spiracular openings. They found that TG
metabolism was not sucient to compensate for water losses under conditions of high CO2
concentration and low ambient humidity.
polysaccharides they identi®ed by electrophoresis were similar to amylose and amylopectin and dierent from glycogen.
Friedlander and Navarro (1979b) measured glycogen concentrations after exposure of E. cautella pupae to hypoxia and hypercarbia and found that hypercarbia increased glycogen utilization. This utilization is more accentuated under hypoxia which is associated with the production of lactate. Glucose levels were not in¯uenced by hypercarbia but rose signi®cantly during exposure to hypoxia. There is a particular interest in understanding the mechanism of utilization of energy reserves in insects under modi®ed atmospheres. In this context, polysaccharides and triacylglycerols are generally considered as the principal energy reserves. Adler (1994) demonstrated that lactate was produced bySitophilus granarius (L.) under anoxic conditions. However, after 24 h, lactate production decreased to almost zero, suggesting the inhibition of this metabolic pathway. It was suggested that the inhibition of glycolysis at low lactate levels is associated with a low energy yield and thereby in atmospheres that combine anoxia and hypercarbia the lethal action is enhanced under the in¯uence of CO2. Although
without O2, glycolysis is dominant, in a few cases, the breakdown of certain amino acids can
be utilized for the production of the energy conserving adenosine triphosphate (ATP). Also, nutritive compounds such as lipids, proteins and carbohydrates can be metabolised with a maximum energy yield in the presence of O2; but the energy yield of anoxic metabolism is
comparatively low. This anaerobic metabolism gives rise to acidic compounds. Therefore, in the application of MAs, a particular interest exists in determining the levels of O2 and CO2 or
their combination that can prevent oxidative metabolism and thereby cause insect death. In the following experiments an attempt was made to elucidate the nature of the main energy reserves, namely polysaccharides and triacylglycerols, in adults of the three strains of T. castaneum, and their importance during exposure to the stresses of hypoxia and hypercarbia.
2. Materials and methods
2.1. Insects
Three strains ofT. castaneum were used. One strain had been selected for resistance to a low O2 content (LOC) atmosphere of 0.5% O2 in nitrogen (N2) at 95% r.h., and another to a high
carbon dioxide content (HCC) atmosphere of 65% CO2, 20% O2 and 15% N2 at 95% r.h.. A
third strain, the original unselected laboratory strain sensitive to both MAs, was also employed. The insects were reared at 268C on ®nely ground wheat and 2.5% brewer's yeast (Donahaye 1990a).
2.2. Triacylglycerol measurements
Concentrations before exposure to MAs: Adults, 15±20 days old, in four groups of 100, were taken from cultures of all three strains at the 23rd generation, weighed, and analyzed for TGs in the following manner:
according to the method of Bucolo and David (1973). The TG concentration was expressed in mg trioleoylglycerol per 100 insects on a dry weight basis (by extrapolation using results of water content analyses at the 21st generation), or mg/100 mg of insect material on a wet basis.
A set of 10 analyses of glycerol concentration in insects after exposure for 24 h to HCC and LOC using the method of Weiland (1975), resulted in an average of 0.3 mmol/g or 0.027% of insect wet weight. Therefore correction for glycerol in calculations of TG concentration was ignored.
Concentrations during exposure to MAs: The exposure experiments were carried out in a standard apparatus designed to mix the components of modi®ed atmospheres in the required proportions, adjust the gas mixtures to 95% r.h. by passing them through wash-bottles containing sulphuric acid, and supply them to sets of 100 ml Erlenmeyer ¯asks at a uniform ¯ow rate of 15 ml/min. per ¯ask, in which the insects were exposed (Donahaye, 1990a). Adults 15±20 days old were taken from cultures of the 24th generation of all three strains. They were divided into groups of 100, weighed and placed in exposure ¯asks. Four groups of the HCC-selected and the unHCC-selected strains were exposed to HCC, and four groups of the LOC-HCC-selected strain and the unselected strain were exposed to LOC for each of the following exposure times: 0, 1, 2, 4, 6, 8, 10, 12, and 14 days. At the end of each exposure time, the insects were removed from the MA exposure apparatus and re-weighed to determine loss in weight. Then TG analysis was carried out as above.
By subtraction of recorded TG concentrations after exposure, from the TG concentrations recorded for insects before exposure, the percent losses in TG, in mg/100 insects, were calculated for each exposure period.
Water content of insects, rates of water loss during exposure, and total dry weight losses were previously examined under HCC and LOC atmospheres for dierent exposure periods (Donahaye, 1992). In the present work these calculated TG concentrations were integrated with the dry weight losses recorded in the previous study.
2.3. Measurement of polysaccharides and glucose
Exposure of the three strains of insects to the MAs was similar to that for
measurement of TGs, and exposure times were the same. Measurements of
polysaccharides, without distinction between glycogen, amylose and amylopectin, and of concentrations of glucose, were carried out by the method of Keppler and Decker (1974).
This method employs amyloglucosidase which speci®cally hydrolyses oligo- and
polyglucosides of the amylose, and glycogen-type, whereas chitin as a source of
polysaccharide was not included in the test.
3. Results
3.1. Triacylglycerol measurements
Before exposure to MAs: t-tests on the results given in Table 1 show that on the basis of weight of TG/100 insects, the dierences in TG between the HCC-selected and the LOC-selected or the unLOC-selected strains were signi®cant, but the LOC-LOC-selected strain did not dier signi®cantly from the unselected strain. However, when the TG of the insects was compared on the basis of 100 mg dry weight, the HCC-selected and the LOC-selected strains both diered signi®cantly from the unselected strain.
During exposure to MAs: Calculated progressive percentage reduction in TG levels during exposure to the HCC and LOC atmospheres, together with mortality results are presented in Figs. 1 and 2 respectively. In order to ensure that the insects only utilized their initial energy reserves, they were exposed to the MAs without food. In both experiments selected and unselected strains were tested.
For the HCC atmosphere, signi®cant dierences were found in TG utilization between selected and unselected strains during exposure. For the unselected strain, the exposure time after which no individuals were able to recover was 4 days, whereas only 85% mortality of the HCC-selected strain was recorded after 14 days exposure to the HCC atmosphere.
For the LOC atmosphere, signi®cant dierences in TG utilization over the ®rst 12 days of exposure were revealed, with a rapid decrease in TG of the unselected strain as mortality increased. At 14 days, mortality of the LOC-selected strain had risen to 70% and a similar TG level was recorded for both strains.
3.2. Concentrations of polysaccharides and glucose
Before exposure to MAs: One-way analysis of variance of recorded polysaccharide levels of the three strains failed to reveal a signi®cant dierence between them (ranging between 2.54 mg/ g for the unselected, 2.99 mg/g for the LOC-selected, and 2.84 mg/g for the HCC selected strains). However, there was a signi®cant dierence (Student's multiple range test) between the initial glucose concentrations of the HCC-selected strain, which averaged 130.5 nmol/g, and the
Table 1
Average triacylglycerol concentrations in adults of three strains ofTribolium castaneum at the 23rd generation of selection
Strain Adult wt (mg/100 insects)a mg TG/100 insects mg TG/100 mg dry wt
HCC-selected 202.2 ab 20.69 a 10.50 a
LOC-selected 208.5 b 13.83 b 6.76 b
Unselected 184.8 c 14.36 b 8.70 c
a
Donahaye (1993).
b
LOC-selected strain, which averaged 91.1 nmol/g, while the unselected strain averaged 117.3 nmol/g.
During exposure to MAs: Figs. 3 and 4 show that the initial quantities of polysaccharide were very low, representing from 0.25% to 0.3% of the wet weight of the insect, and formed a minor energy source in comparison with TGs. During exposure to HCC or to LOC, polysaccharide concentrations of both selected and unselected strains dropped to up to half their initial levels after 14 days exposure. This slow decrease indicates that the glycolytic pathway is not of major importance during exposure of T. castaneum to either of the MAs tested.
Simultaneous with the drop in polysaccharide levels, the glucose concentrations shown in Figs. 5 and 6 rose considerably during the ®rst days of exposure, both to HCC and to LOC. In both cases the rise in glucose concentration was greater for the unselected than for the selected strains. After 14 days exposure, glucose levels had dropped to levels similar to those recorded initially.
Fig. 2. Rates of utilisation of triacylglycerols and mortality of Tribolium castaneum during exposure of the low (0.5%) oxygen concentration-selected, and unselected strains to the low oxygen concentration atmosphere.
Fig. 4. Changes in polysaccharide concentration of Tribolium castaneum during exposure of low (0.5%) oxygen-selected, and unselected strains to the low oxygen concentration atmosphere.
4. Discussion
The results of TG concentrations inT. castaneum before exposure to MAs may be compared to those of Villeneuve and Lemonde (1963), who measured free lipids (petroleum ether extract) and recorded 25.2 mg/100 adult insects of T. confusum (4±5 days old), or 12.1 mg/100 mg insect dry wt. The ®nding that the heavier LOC-selected strain did not show a proportional increase in TG content, (in contrast to the HCC-selected strain), was not explained by tests to show the presence of other energy reserves. However a possible conjecture is that an increased resistance to desiccation may be imparted by enhanced cuticular characteristics or by increased body size which reduces the ratio of surface area to volume.
From Fig. 1 it can be seen that exposure to HCC was accompanied by rapid utilization of TGs. For the unselected strain about 85% of the TGs had disappeared within 6 days. More prolonged exposure did not decrease TGs further, probably because total mortality occurred after about 6 days (taking into account the fact that mortality analysis does not determine the times at which death occurs, but rather the times at which the insects reach a point of no-recovery). For the HCC-selected strain the decrease in TG concentration was slower. After 14 days of exposure, nearly 5% of the TGs remained and mortality had reached 85%.
To summarize, Table 2 was prepared to enable comparison between the average initial TG concentrations and dry weights (DW) in adults of the HCC-selected and unselected, and the LOC-selected and unselected strains, with those after exposure to the HCC and LOC atmospheres respectively, at the 10th day. The Table shows that for the 10-day exposure period, the total dry weight loss of the HCC-selected strain was just over 30% with the major part being caused by reduction in TGs. Also shown is an additional dry weight loss of 13%
indicating that energy from another unidenti®ed source was being utilized by the HCC-selected strain, whereas in the unselected strain all dry weight loss was accountable by utilization of TGs.
A further aspect of the dierence in TG utilization between the two strains lies in their dierence in ability to maintain water balance during exposure (Donahaye, 1992, 1993). Clearly, the ability to control the loss of metabolic water through steady and moderate utilization of TGs in the HCC-selected strain, prolongs its survival during exposure. In comparison, the unselected strain consumed its TG reserves under HCC within the ®rst 6 days, and underwent rapid and continuous desiccation in spite of the high ambient humidity of 95%. The comparison in DW loss at the 10th day exposure (Table 2) also shows the eective use of TG reserves and the ability to control water loss in the HCC-selected but not in the unselected strain.
Losses in TG of both the LOC selected and unselected strains during exposure to LOC were much more moderate and although they were clearly a source of energy reserve during exposure, with utilization by the unselected strain being more rapid, there was no clear indication that mortality ensued when TG reserves were fully utilized. Calculations indicate
Table 2
Comparison of average triacylglycerol concentrations and dry weights (DW) in adults of the HCC-selected and unse-lected, and the LOC-selected and unselected strains, exposed to the HCC atmosphere and LOC atmosphere respect-ively, at the 10th day of exposure (all data based on 100 insects)
Initial weight Final weight Loss in weight
(mg)2SD (mg)2SD (mg) % loss in weight
(a) HCC atmosphere (65 vol% CO2, 20 vol% O2, 15 vol% N2at 268C) HCC-selected strain:
DW without TG 77.1821.323 65.1821.365 13.36 13.00
TGs 20.6923.211 2.9020.413 16.44 79.46
Total DW 97.8721.323 68.0121.721 29.80 30.45
Water 98.721.334 65.521.679 33.2 33.6
Unselected strain:
DW without TG 65.8820.454 67.4824.886 ÿ0.83 ÿ3.75
TGs 14.3421.085 1.7220.138 11.92 82.72
Total DW 80.2920.454 69.2024.989 11.09 13.84
Water 99.7320.564 47.6222.138 52.12 52.26
(b) LOC atmosphere (99.5 vol%N2, 0.5% vol O2at 268C) LOC-selected strain:
DW without TG 79.4921.200 74.6121.516 3.22 2.73
TGs 13.8322.184 8.6220.349 6.86 44.33
Total DW 93.3221.200 83.2321.213 10.09 10.8
Water 117.4621.511 109.3621.359 8.10 6.89
Unselected strain:
DW without TG 65.2221.176 58.8122.588 8.00 5.43
TGs 14.3621.003 2.7320.639 9.98 69.22
Total DW 79.5221.176 61.5522.684 17.98 22.62
that both strains also used other sources of energy reserve during exposure (Table 2). Weight loss experiments (Donahaye, 1992) showed that water loss during exposure to LOC was not critical. It may be assumed therefore that the TGs were a source of energy during aerobic metabolism under exposure to LOC, and that the more rapid utilization of TG in the unselected strain was due to its higher metabolic rate during exposure.
In conclusion, it was shown previously (Donahaye, 1992) that for exposure to hypercarbia, and even to hypoxia of 0.5% O2, metabolism of the three strains was mainly aerobic and that
duration of survival was correlated with their rates of metabolism during exposure and ability to conserve water. The present ®ndings show that TGs form the principal energy source for metabolism during exposure. The greater quantities of TG in the HCC resistant strain and its lower rate of metabolism, enable it to survive longer under hypercarbia, and this appears to be an important mechanism of resistance. Under hypoxia, as mortality progressed, energy reserves of TG still remained relatively high and their depletion does not appear to limit survival of either strain. Possibly mortality ensues when individuals are no longer able to maintain aerobic metabolism.
An immediate drop in polysaccharide level during the ®rst 48 h is apparent for all strains exposed to HCC and LOC. For the HCC-selected strain there is a temporary recovery after 48 h (Fig. 3) which indicates glycogen production from other polysaccharide sources, possibly chitin. However, this point needs further attention. The levels of glucose only provide information on the relation between its rate of production and its rate of consumption. This can explain why the level of glucose rose when polysaccharide levels fell, and then later declined.
Acknowledgements
Thanks are due to the late Dr A. Friedlander of this Department for his guidance in the biochemical analyses. The study was funded by a grant from the US±Israel Binational Agricultural Research & Development Fund (BARD). We are grateful to Miriam Rindner and Mr A. Azrieli for their technical assistance.
References
Adler, C.S., 1994. Carbon dioxide Ð more rapidly impairing the glycolytic energy production than nitrogen? In: Highley, E., Wright, E.J., Banks, H.J., Champ, B.R. (Ed.). Proceedings of the 6th International Working Conference on Stored Products Protection, Canberra, Australia, vol. 1, pp. 7±10.
Annis, P.C. 1987. Towards rational controlled atmosphere dosage schedules: a review of current knowledge. In: Donahaye, E., Navarro, S. (Eds.), Proceedings of the 4th International Working Conference on Stored Product Protection, Tel Aviv, Israel, pp. 128±148.
Banks, H.J., 1994. Fumigation ± an endangered technology? In: Highley, E., Wright, E.J., Banks, H.J., Champ, B.R. (Ed.). Proceedings of the 6th International Working Conference on Stored Products Protection, Canberra, Australia, vol. 1, pp. 2±6.
Bligh, E.G., Dyer, W.J., 1959. A rapid method of total lipid extraction and puri®cation. Canadian Journal of Biochemistry and Physiology 37, 911±917.
Bond, E.J., Buckland, C.T., 1979. Development of resistance of carbon dioxide in the Granary Weevil. Journal of Economic Entomology 72, 770±771.
Bucolo, G., David, H., 1973. Quantitative determination of serum triglycerides by the use of enzymes. Clinical Chemistry 19, 475.
Delmenico, R.J. 1993. Controlled atmosphere and fumigation in Western Australia Ð a decade of progress. In: Navarro, S., Donahaye, E. (Eds.), Proceedings of an International Conference on Controlled Atmosphere and Fumigation in Grain Storages, Winnipeg, Canada, pp. 3±12.
Donahaye, E., 1990a. Laboratory selection of resistance by the red ¯our beetleTribolium castaneum (Herbst) to an atmosphere of low oxygen concentration. Phytoparasitica 18, 189±202.
Donahaye, E., 1990b. Laboratory selection of resistance by the red ¯our beetle Tribolium castaneum(Herbst) to a carbon dioxide enriched atmosphere. Phytoparasitica 18, 299±308.
Donahaye, E., 1992. Physiological dierences between strains ofTribolium castaneum(Herbst) selected for resistance to hypoxia, a strain selected for resistance to hypercarbia and the unselected strain. Physiological Entomology 17, 219±229.
Donahaye, E., 1993. Biological dierences between strains ofTribolium castaneum(Herbst) selected for resistance to hypoxia, and hypercarbia and the unselected strain. Physiological Entomology 18, 247±250.
Edney, E.B., 1967. Water balance in desert arthropods. Science 156, 1059±1066.
EPA, 1998. Notice of availability of the Aluminium amd Magnezium phosphide reregistration eligibility decision document. Environmental Protection Agency, Federal Register Document December 23 1998, 63, (246) 71123± 71126.
Friedlander, A., Navarro, S., 1979a. The eect of controlled atmospheres on carbohydrate metabolism in the tissue ofEphestia cautella(Walker) pupae. Insect Biochemistry 9, 78±83.
Friedlander, A., Navarro, S., 1979b. Triacylglycerol metabolism in Ephestia cautella pupae exposed to carbon dioxide. Experientia 35, 1424±1425.
Friedman, S., 1970. Metabolism of carbohydrates in insects. Chemical Zoology 40, 403±408.
Gilbert, L.I., 1967. Lipid metabolism and function in insects. Advances in Insect Physiology 4, 69±211.
Kennington, G.S., Cannell, S., 1967. Biochemical correlates of respiratory and developmental changes in anoxic Tribolium confusumpupae. Physiological Zoology 40, 403±408.
Keppler, D., Decker, K. 1974. Glycogen determination with amyloglucosidase. In: Bergmeyer, H.U. (Ed.), Methods of Enzymatic Analysis. Academic Press, New York, pp. 1127±1131.
Longsta, B.C., 1994. The management of stored product pests by non-chemical means: an Australian perspective. Journal of Stored Products Research 30, 179±185.
Navarro, S., Dias, R., Donahaye, E., 1985. Induced tolerance ofSitophilus oryzae adults to carbon dioxide. Journal of Stored Products Research 21, 207±213.
UNEP, 1995. Report of the methyl bromide technical options committee Ð 1995 Assessment. Montreal Protocol on substances that deplete the ozone layer, Kenya 1994, p. 304 pp.
Villeneuve, J.L., Lemonde, A., 1963. Variations des lipides au cours de la metamorphose de Tribolium confusum Duval. Archives Internationales de Physiologie et de Biochimie 71, 143±154.
Villeneuve, J.L., Lemonde, A., 1965. Les glucides de Tribolium confusum Duval. I Identi®cation. Archives Internationales de Physiologie et de Biochimie 73, 681±688.
Weiland, O. 1975. Glycerol. In: Bergmeyer, H.U. (Ed.), Methods of Enzymatic Analysis. Academic Press, New York, pp. 211±214.